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EC number: 224-116-8 | CAS number: 4203-89-8
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Endpoint summary
Administrative data
Description of key information
Three acute studies for three trophic levels are available.
The acute fish endpoint is fulfilled using Weight of Evidence. An OECD 236 (FET) study of substance 4203-89-8 gave an LC 50 of > 100 mg/L. It was demonstrated that 4203-89-8 rapidly hydrolyzes (see 5.1.2) to 108-94-1 and 51706-72-0/45011-26-5. The FET result is in line with ECOSAR results for the hydrolysis byproducts (all LC 50 > 100 mg/L).
The acute toxicity of 2 -(1 -oxa-4 -azaspiro[4.5]dec-4 -yl)ethyl methacrylate to invertebrates was determined in an OECD 202 study. In a limit test at 100 mg/L no effects were found and the EC50 is greater than 100 mg/L (nominal). This is equal to a geometric mean measured concentration of 34.6 mg/L cyclohexanone. Initial concentration cyclohexanone was 37.7 mg/L, which is similar to the theoretical maximum amount of 38.7 mg/L that can be formed when 100 mg/L parent substance degrades.
From these results it can be shown that the parent substance was fully hydrolyzed at test start and test animals were exposed to cyclohexanone and 2-[(2-hydroxyethyl)amino]ethyl 2-methylacrylate.
100 mg/L parent substance is equal to 68.4 mg/L 2-[(2-hydroxyethyl)amino]ethyl 2-methylacrylate.
The toxicity of 2-(1-oxa-4-azaspiro[4.5]dec-4-yl)ethyl methacrylate to freshwater algae was determined in an OECD 201 study. The effect of the test item on the growth of Pseudokirchneriella subcapitata has been investigated over a 72 hour period and based on the nominal parent test concentrations gave the following results: 72h-ErC50 = 88 mg/L.
The 100 mg/L nominal test concentration is equal to a geometric mean measured concentration of 36.4 mg/L cyclohexanone. Initial concentration cyclohexanone was 39 mg/L, which is similar to the theoretical maximum amount of 38.7 mg/L that can be formed when 100 mg/L parent substance degrades.
From these results it can be shown that the parent substance was fully hydrolyzed at test start and test animals were exposed to cyclohexanone and2-[(2-hydroxyethyl)amino]ethyl 2-methylacrylate.
The 72 -hErC50 is equal to 60.2 mg/L 2-[(2-hydroxyethyl)amino]ethyl 2-methylacrylate.
The toxicity of 2-(1-oxa-4-azaspiro[4.5]dec-4-yl)ethyl methacrylate to activated sludge was determined in an OECD 209 study under GLP. From the results EC values were calculated. The EC10, EC20, EC50and EC80values of the substance for activated sludge after 3 hours contact time are all >1280 mg/L, the highest concentration tested. 2-(1-oxa-4-azaspiro[4.5]dec-4-yl)ethyl methacrylate is therefore considered not harmful to activated sludge.
Additional information
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